Abstract:
Sri Lanka, despite its small size, possesses a high level of biological diversity. Both
the coastal and seashore vegetation covers a good part of the coastline. Mangroves
occur near river mouths and on the shores of lagoons. Salt marsh vegetation is
found on mud flats, which are periodically inundated with seawater. According to
the inventory prepared by FAO/UNDP in 1983, the total area under mangrove
vegetation in Sri Lanka was about 8000 ha but in 1992 the forest map estimated it
as 6877 ha (1UCN, 1993). About 60% of these mangroves are found in Puttalam,
Kalpitiya, Portugal, Dutch Bays and the rest in Trincomalee, Jaffna, Koggala,
Kalametiya and Kokillai.
High diversity of faunal and floral composition and their interactions can be seen in
mangrove forests. These faunal and floral components play a vital role in
determining the status of the mangroves. When we consider the importance of
mangrove crabs, as a constituent group of the fauna, it seems to have a high
contribution towards the health of the mangrove vegetation. The role that
mangrove crabs play in determining the structure and function of tropical
mangrove forests is, however, an issue, which spans both perspectives. Smith el aI.
in 1991 working on Sesarmid crabs in Australian mangrove forests have
highlighted the important effects of these invertebrates imposed on the carbon
cycling in the mangrove communities, and on the structure of the forests. Most
species occurring in non-inundated areas (that could be inundated) make burrows
to live. Present study was carried out in Galle, Rekawa, Negombo and Pambala.
The results reveal that the densities of the burrows vary significantly according to
the zone occurrence (Rhizophora, Excoecciria, Open area and Mixed zone) and the
location of the study sites (Galle, Rekawa, Negombo and Pambala) at 5%
significant level. Numbers of crabs occupying a 1 m2 space also varied from zone-to-zone and site vise. This variation was also significant at 5% level. Numbers of
crabs occupying a 1 m2 space also varied with the time. The physical and chemical
parameters such as temperature, RH, pH, salinity also varied with the time of
33
Zoology Special Abstracts
observation and the zone occurrence. Correlations between the numbers of crabs
occupying a I m2 space and the various physical and chemical parameters of the
sites did not have a significant relation at 5% level. There can be a correlation
between interaction effects of these parameters and numbers of crabs occupying a I
m2 of space, which has to be further investigated. However the results show that
the numbers of crabs occupying a 1 m2 space during the daytime and the air
temperature was significantly correlated in Open area located in Galle. The soil
texture also varied from zone-to-zone in Galle. But a uniform muddy mixed sandy
substrate was observed in Rekawa. Number of crab species found in Rhizophora
zone, Excoecaria zone and Open area are respectively 13, 4 and 8 in Galle.
Carcinoma carnifex was found in both Excoecaria zone and Open area while
Neosamatium meinerti was found in both Rhizophora and Excoecaria zones in
Galle mangrove forest. Number of species found in the Mixed zone in Rekawa,
Negombo were 3 and 4 respectively, where as that recorded in Excoecaria zone in
Pambala was 4.
The density of burrows also varied significantly depending on the location.
According the mean number and the standard error of the density of the burrows
recorded at the Mixed zone in Rekawa and Negombo were 2.1 ± 0.1667 and 7.3333
± 0.4216 respectively. While that recorded in Excoecaria zone in Pambala was 7 ±
0.4472 m A significant difference between the number of crabs occupying in a 1
m2 space during daytime in Excoecaria zone in Galle and Pambala was also
evident (t = 4.727, df = 17, p < 0.001) and there was also a significant difference
between the numbers of crabs in 1 m2 of space during daytime in Mixed zones in
Rekawa & Negombo (t = -3.352, df = 22, P < 0.01) was evident.